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Adapting to Climate Change: Assessing the World Bank Group ...

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APPENDIX HADDITIONAL EVIDENCEkilometer of forest based on those areas that were protected, while ignoring <strong>the</strong> factthat <strong>the</strong> average benefit of avoided losses depends on <strong>the</strong> value of assets protected,which will not remain constant outside of <strong>the</strong> sample zone where mangroves wereplanted. Barbier (2007) uses an expected damage function approach that estimates<strong>the</strong> value of coastal protection benefits based on coastal disaster data and mangrovecoverage from Thailand, and find much lower values than are generated from areplacement cost approach. But weaknesses in <strong>the</strong> available data on disasterdamage, mangrove coverage, and o<strong>the</strong>r fac<strong>to</strong>rs that drive disaster losses suggest that<strong>the</strong>ir point estimate (loss of one square kilometer of mangrove leads <strong>to</strong> an increase ofexpected s<strong>to</strong>rm damages of $585,000) should be interpreted with caution.Efforts <strong>to</strong> estimate <strong>the</strong> coastal protection benefits of mangroves are complicated by ahigh degree of spatial variation in impact, depending on <strong>to</strong>pography, vegetationproperties, and <strong>the</strong> types of s<strong>to</strong>rms involved. For example, Kabir and o<strong>the</strong>rs (2006)model <strong>the</strong> effect mangroves in reducing s<strong>to</strong>rm surge from a 1970 cyclone on HatiaIsland in Bangladesh. They find that while in some locations mangrove afforestationwith a width of 133-600 meters leads <strong>to</strong> reduction in s<strong>to</strong>rm surge height of 0.18-0.45meters, in o<strong>the</strong>r locations <strong>the</strong> protective benefits were negligible. Mazda and o<strong>the</strong>rs(1997) study mangrove zone on <strong>the</strong> Tong King delta in Vietnam, and find nosignificant reduction in s<strong>to</strong>rm surge in areas with immature mangrove cover, butwave height reduction of 20 percent per 100 meters of mangrove in areas withsufficiently tall trees. Badola and Hussain (2005) measure economic losses in threevillages in Orissa hit by a 1999 cyclone, and find <strong>the</strong> greatest loss per household wassuffered in a village with an embankment but no mangroves ($153.74), followed by avillage with no embankment and no mangroves ($44.02) with <strong>the</strong> least damageoccurring in a village with mangroves ($33.31). The fact that a given s<strong>to</strong>rm has suchdrastically different effects on different villages (even those close <strong>to</strong> each o<strong>the</strong>r)makes it difficult <strong>to</strong> estimate <strong>the</strong> marginal value of mangrove cover because of <strong>the</strong>economic and geographic heterogeneity at <strong>the</strong> village level Das and Vincent(2009)evaluated <strong>the</strong> protective effect of mangroves for <strong>the</strong> same cyclone over a wider area,using geographical data on geophysical and socioeconomic fac<strong>to</strong>rs. They found thatmangroves had a statistically significant protective effect and on average, for thisevent, one hectare of mangroves averted 0.0148 deaths.127

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